a review of the current knowledge of rodent behaviour in relation to
TRANSCRIPT
A review of the currentknowledge of rodent behaviourin relation to control devices
B. Kay Clapperton
SCIENCE FOR CONSERVATION 263
Published by
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Cover: Rat emerging from rat tunnel with poison bait in mouth, Breaksea Island, Fiordland National
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© Copyright March 2006, New Zealand Department of Conservation
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CONTENTS
Abstract 5
1. Introduction 6
1.1 Background 6
1.2 Interpretation 7
1.3 Objectives 8
2. Methods 8
3. Results 9
3.1 Taste preferences and lures 93.1.1 Bait bases 93.1.2 Sugars and oils 113.1.3 Other additives and lures 123.1.4 Formulations 133.1.5 Hardness 133.1.6 Wrappings 143.1.7 Colour 143.1.8 Gnaw sticks 14
3.2 Meal size 14
3.3 Neophobia 15
3.4 Feeding behaviour 17
3.5 Social behaviour 18
3.6 Movements and home range 19
3.7 Territoriality 22
3.8 Responses to bait stations 22
3.9 Other factors 233.9.1 Behavioural resistance 233.9.2 Bait shyness and poison aversion 243.9.3 Resistance 243.9.4 Odours 253.9.5 Repellents 253.9.6 Grooming 263.9.7 Responses to traps 263.9.8 Practical matters 26
4. Discussion and conclusions 27
5. Acknowledgements 28
6. References 29
Appendix 1 47
Combinations of words used in the STNeasy searches 47
Appendix 2 48
Further bibliography 48
5Science for Conservation 263
A review of the currentknowledge of rodent behaviourin relation to control devices
B. Kay Clapperton
49 Margaret Avenue, Havelock North, New Zealand
A B S T R A C T
A recent review of techniques used to detect and control the four introduced
rodent species found on the New Zealand mainland and islands (house mice
Mus musculus, ship rats Rattus rattus, Norway rats Rattus norvegicus and
kiore Rattus exulans) identified the need for better understanding of rodent
behaviour. This report provides a review of the published literature on rodent
behaviour in relation to control devices, especially bait stations and baits. The
review is based on searches of computer databases and information from key
researchers on: taste preferences, meal size, neophobia, feeding behaviour,
movements, home ranges and territoriality, bait shyness, aversion, resistance,
odours, and colour preference. Other aspects of rodent behaviour, including
responses to repellents, sounds and traps, are also briefly summarised.
Keywords: rodent, rat, mouse, Rattus rattus, Rattus norvegicus, Rattus
exulans, Mus musculus, eradication, control, island, bait, station, behaviour,
neophobia, feeding, movement, aversion, resistance
© March 2006, Department of Conservation. This paper may be cited as:
Clapperton, B.K. 2006: A review of the current knowledge of rodent behaviour in relation to
control devices. Science for Conservation 263. 55 p.
6 Clapperton—Rodent behaviour in relation to control devices
1. Introduction
1 . 1 B A C K G R O U N D
This project is a search for current knowledge of rodent behaviour in relation to
control devices. The four species of introduced rodents found in New Zealand are
the Norway (or brown) rat (Rattus norvegicus; Berkenhout, 1769), the ship rat
(Rattus rattus; Linnaeus, 1758) (commonly also referred to as the roof rat or
black rat), kiore (Rattus exulans; Peale, 1848) (also known as the Pacific rat or
Polynesian rat) and the house mouse (Mus musculus; Linnaeus, 1758). All four
species cause damage to the native New Zealand flora and/or fauna and are the
subject of control programmes by the New Zealand Department of Conservation
(DOC). They pose particular threats to island biota (Moors et al. 1992).
Since the late 1970s, rodents have been eradicated from an increasing number
of islands around New Zealand and elsewhere (Veitch & Bell 1990; Taylor et al.
2000; Clout & Veitch 2002; Thomas & 2002; Towns & Broome 2003). While
New Zealanders are world leaders in rat eradication techniques, particularly on
islands, only 61% of mouse eradication attempts in New Zealand from 1980 to
the 1990s were successful (Cleghorn & Griffiths 2002, Towns & Broome 2003;
Clout & Russell 2005). Rodent control techniques used in New Zealand have
been developed primarily with rats as the target species. Successful removal of
mice has been limited to islands of 200 ha or less (Hook & Todd 1992; Brown
1993; McKinlay 1999; Veitch 2002b), with the exception of Enderby Island (800
ha) (Amori & Clout 2003), where the main target for eradication was the rabbit
(Oryctolagus cuniculus) (Torr 2002). The need for mouse-specific control
techniques is best summaried by Pursley (1989): ‘Establishing controls for
either mice or rats is as different as comparing apples and oranges’.
The second aspect of island management that still eludes us is the confidence
that we can detect and then eliminate rodents when they first invade (or re-
invade) island sanctuaries. These rodents are highly commensal and common
around wharves and foreshore areas, and can easily stow away on ships or swim
to islands. On reaching rodent-free islands, incoming rodents are often faced
with a range of foods and little competition. Because of their particular
behavioural traits and ability to rapidly increase their population, the risk of
rodents establishing on islands is high. Mice and rats are also good climbers, so
have impacts on arboreal as well as ground habitats when they do reach islands.
The potential effects of rodents re-establishing on islands from which they have
been removed could be catastrophic. Dilks & Towns (2002) list some ‘scares’
and ‘near-misses’ that illustrate this concern. Large investments in time and
money have been made in clearing islands and the early detection and removal
of invading rodents is vital. Most of the baits and delivery systems currently
used for controlling rodents have not been comprehensively evaluated to see
how attractive they are to those animals that arrive on islands with an
abundance of food. The risk of invasion and undetected spread is well
illustrated by Frégate Island, Seychelles (Thorsen et al. 2000). Towns & Broome
(2003) give some examples of new invasions and re-invasions by rodents of
islands in New Zealand. They specify the lack of knowledge of invasion
7Science for Conservation 263
behaviour and lack of tools for effectively intercepting invasions as significant
impediments to advances in island conservation (see also Dilks & Towns 2002;
McClelland 2002b).
Improved understanding of rodent behaviour is also vital for planning eradication
of long-established rat populations on New Zealand islands and for rodent control
on the mainland, and on other islands elsewhere in the world (Sowls & Byrd 2002;
Amori & Clout 2003; Courchamp et al. 2003; Abdelkrim et al. 2005).
There is a vast literature on the biology and behaviour of rodents (e.g. reviews
by Ewer 1971; Rowe 1973; Berry 1981; Mackintosh 1981; Meehan 1984; Barnett
1988; Prakash 1988; Buckle & Smith 1994; Macdonald et al. 1999b; Singleton et
al. 1999). This is because mice and laboratory rats (R. norvegicus) are used
extensively in medical and psychological research, and these commensal
rodents are pests world-wide. The ship rat has been studied because it is a
widespread pest. While kiore are also considered to be a pest in some places,
there is little known about their behaviour, especially in New Zealand. Atkinson
& Towns (2001) do not list any information on behaviour in their review of
advances in our knowledge of the species between 1990 and 2000.
1 . 2 I N T E R P R E T A T I O N
When interpreting the information in the literature about rodent behaviour, the
history of these species must be considered. The domestication of laboratory
rats has had a marked impact on their behaviour (Galef 1970; Shepherd & Inglis
1987; Kotenkova et al. 2003). One of the most studied behavioural differences
between domesticated and wild strains of rats is their level of neophobia. While
the commensal rat species are thought to have developed their fear of new
objects in their familiar environment because of their association with people,
‘lab’ rats are thought to have lost this neophobia (Barnett & Cowan 1976;
Mitchell 1976; Cowan 1977a). Barnett (1956) noted that ‘wild’ Norway rats
have a greater behavioural repertoire than albino rats, and Barnett & Spencer
(1953a) noted differences in food preferences between wild and albino rats. We
must also differentiate between commensal rats and those living with no
contact with people, as is often the case in New Zealand. Little is known about
the relative levels of neophobia or other differences in behaviour between truly
wild and commensal rats, but it is possible that populations long isolated from
human contact will not show the same neophobia as commensal populations
(Taylor & Thomas 1989). This is certainly true for rodent species that do not
live commensally (Cowan 1977a; Brammer et al. 1988). Therefore, while
Macdonald et al. (1999b) give an excellent review of the behavioural ecology of
Rattus norvegicus, it should be remembered that it is based on the study of
commensal populations.
The impact of domestication appears to be less for mice (MacKintosh 1981), but
Klimstra (1972) warns that much of the data on behaviour of albino mice has
little application in the field. Bronson (1979) suggested that commensal and
feral populations of mice differ in many characteristics including social
organisation. While mice are generally neophilic (Barnett 1988), Kronenberger
& Médioni (1985) argue that wild mice may have rapidly evolved neophobia
because of man’s fight against rodents.
8 Clapperton—Rodent behaviour in relation to control devices
There can even be differences between different populations of wild rodents
(Mitchell et al. 1977). Invasions are often established from one or a few
dispersing individuals, so genetic differences between rats could result in
substantial phenotypical differences on different islands. Closed populations of
mice have been shown to have a deficiency of heterozygotes, while larger
populations are genetically variable (Berry 1970). Closed island populations can
be expected to show differences in behaviour and population dynamics from
populations open to migration, including differences in spatial organisation
(Gliwicz 1980). We must also consider the importance of differences in habitat,
climate and history of control when drawing generalisations or comparisons
amongst the studies referred to in this review.
1 . 3 O B J E C T I V E S
The objective of this study was to summarise the current knowledge of rodent
behaviour in relation to control devices, by searching recent literature and
contacting key researchers on rodent behaviour and control.
To provide a framework for this search, seven key questions were identified:
• Do rodents have different taste preferences? What are they?
• What lures are known to be attractive to the different rodent species?
• Does the degree of neophobia vary between rodent species? Is there any
evidence that neophobia can vary throughout the year, with population
density or food supply?
• What is the meal size of the different rodents?
• What is known about behaviour of rats in relation to bait stations (e.g.
Norway rats like to sit on their haunches when eating bait)? Is anything
known about colour preference in rodents?
• How do the movements and home ranges of the species relate to commonly-
used bait station spacings?
• What other possible behavioural factors are relevant to rodent control (e.g.
poison shyness, resistance)?
2. Methods
To search for current knowledge of rodent behaviour in relation to control
devices, I conducted computer-based searches of the published literature and
made personal contact with key researchers in New Zealand and other
countries. Topics covered included food and bait preferences, bait palatability,
spacing systems, investigatory behaviours, feeding behaviour, neophobia, bait
size, and bait station designs. I also specifically targeted research on rodents on
islands and island eradication programmes. Some incidental information on
habitat use on islands is included, but the review does not cover the ecology of
the rodent species in depth (nor is the literature on decision analysis regarding
9Science for Conservation 263
when to attempt rodent eradication included (see Harwood 2000; Maguire
2004; Park 2004; Iwatsuki et al. 2005). The computer searches were done
through http://STNeasy.cas.org. I specified the Life Sciences category with the
following databases: BIOSIS, BIOTECHNO, CABA, Caplus, EMBASE and
SCISEARCH. The various combinations of words in the searches are listed in
Appendix 1. I also scanned the literature lists of the papers targeted by these
searches, and received literature lists and reprints from individual researchers.
Potentially useful papers found during the search but not referred to in the text
are included in Appendix 2.
3. Results
3 . 1 T A S T E P R E F E R E N C E S A N D L U R E S
Meehan (1984) cautioned that ‘it is impossible to say which particular foodstuff
will be preferred by individual rats or even whole populations—there is no such
thing as a universally acceptable bait’. Rowe (1973) made a similar comment
about mice. These statements have been confirmed by studies of consumption
of foods by wild rats (Clark 1982). Lund (1988b) gave a general summary of the
ideal characteristics of rodent baits and additives. No magical additives that
made baits irresistible were identified. Marsh (1988) summarised the value of
bait additives: ‘Sugars and vegetable oils and animal fats are the most universally
effective additives for cereal baits to improve acceptance and palatability.
Flavour additives to baits have often decreased rather than increased
consumption’. Bait materials and lures that have been shown to be attractive or
palatable to the four rodent species are listed in Table 1.
3.1.1 Bait bases
While rodents will eat most seed types, various studies have found preferences
for particular seed or grain baits. Whole canary seed is particularly attractive to
wild-strain mice, while pinhead oatmeal and wheat were well accepted (Rowe
et al. 1974). Pennycuik & Cowan (1990) reported that part wild-strain mice
found canary seed, maize and sunflower seeds palatable. Canary seed was again
one of the most palatable foods, along with soft wheat and rice in a study of
mice in Australia (Robards & Saunders 1998). In Egypt, mice preferred wheat to
sorghum, sunflower seeds and bran + 5% molasses (Asran 1993a, b). While
canary seed is highly palatable to mice, its small size limits its application in the
field. This could be overcome by pelleting the grain with just enough propylene
glycol to act as a binder (Robards & Saunders 1998). Pellets are acceptable to
mice in the field (Jacobs et al. 2003), but can easily crumble and lose their
attractiveness when wet (Twigg & Kay 1992; Robards & Saunders 1998).
Yabe (1979) found that ship rats principally ate fruit and seeds. Among a variety
of seeds, millet was highly preferred by commensal ship rats (Khan 1974).
Boiled rice has been recommended for Rattus rattus and R. exulans in Burma
(Harrison & Woodville 1950).
10 Clapperton—Rodent behaviour in relation to control devices
Norway rats in a study displayed extreme omnivory (Yabe 1979). Wild Norway
rats have been shown to prefer wheat meal to whole wheat, white flour or
wheat germ (Barnett & Spencer 1953a), and whole wheat to barley or sausage
rusk (Barnett & Spencer 1949). Wild Norway rats caught from refuse dumps and
a poultry shed preferred sweet rice, proso millet, peanuts, barley and sunflower
seeds to corn (Brooks & Bowerman 1973). They disliked peas, buckwheat,
sesame, lentils and raw soybeans. Cooking the soybeans inactivates the bitter
protein soyin that causes the dislike. The general preference was for grains of
low protein, high carbohydrate and moderate fat or seeds of high protein, low
carbohydrate and high fats. The presence of high levels of the starch
amylopectin may be the key to the attractiveness of sweet rice to Norway rats
(Brooks & Bowerman 1973). Smythe (1976) recommended that composite baits
contain 25% protein. Malting (steeping, germinating and drying) the grain can
increase carbohydrate content, which has been shown to greatly increase bait
acceptance (Nolte 1999).
BAIT/LURE MICE SHIP NORWAY KIORE REFERENCES
RATS RATS
Canary seed × Rowe et al. 1974; Robards & Saunders 1998; Pennycuik & Cowan 1990
Oats × × Rowe et al. 1974; McFadden 1984
Wheat × × Barnett & Spencer 1949, 1953; Rowe et al. 1974; Asran 1993a, b
Rice × × × Harrison & Woodville 1950; Brooks & Bowerman 1973; Khan 1974
Millet × × Brooks & Bowerman 1973; Khan 1974
Barley × × Brooks & Bowerman 1973; McFadden 1984
Maize × × McFadden 1984; Pennycuik & Cowan 1990
Sunflower seed × × Brooks & Bowerman 1973; Pennycuik & Cowan 1990
Peanuts × Brooks & Bowerman 1973
Cooked soybean × Brooks & Bowerman 1973
Sugars × × × Rowe 1961; Collier & Bolles 1968; Howard et al. 1972; Smythe 1976
Saccharin × Wagner 1971
Oils × × × Rowe et al. 1974; Ahmad et al. 1974; Meehan 1984; Pathak & Saxena 1995
Coconut × × × McFadden 1984; Bull 1972; Robertson et al. 1998
Agar × Moro 2002
Fishmeal × Robards & Saunders 1998
Chocolate × × Singh 2003; Weihong et al. 1999
Onion × Saxena et al. 1995
Egg (yolk, shell) × × Shafi et al. 1990,1992; Pervez et al. 1999
Yeast × × Shafi et al. 1990, 1992
Cheese × Weihong et al. 1999
Soap × Weihong et al. 1999
Grape × Smythe 1976
Blood & offal × Bull 1972
Cinnam-aldehyde × Bull 1972
Fish × Bull 1972
Raspberry × Bull 1972
Aniseed × Bull 1972
Banana × McFadden 1984
Eucalyptus × McFadden 1984
Vanilla × McFadden 1984
Clove × McFadden 1984
TABLE 1 . SUMMARY OF BAIT MATERIALS AND LURES ATTRACTIVE AND/OR PALATABLE TO MICE AND RATS.
PALATABILITY INDICATED BY × .
11Science for Conservation 263
Barley, oats and, to a lesser extent, maize, were readily accepted by kiore
(McFadden 1984). Seasonal variation has been reported, with a change to more
nutritious food in autumn (Nieder 1986).
3.1.2 Sugars and oils
Using a conditioned food aversion technique (Reidinger et al. 1983; Stewart et
al. 1983; Mason et al. 1985), Mason et al. (1991) determined that toxicants
cannot be simply classed as bitter, sweet, sour or salty, but have complex
flavours to which rodents respond. Bullard et al. (1977) used the responses of
Philippine ricefield rats (Rattus rattus mindanensis) to show that intensifying
the flavour cues of familiar or favoured foods could be a useful way of
enhancing bait take. So-called attractants help to keep rodents feeding longer at
food sources. They may be effective because they mask the taste of a
rodenticide and/or they are palatable in their own right (Meehan 1984).
Sugar is a well-known effective additive for rats and mice, while bitter flavours
tend to be rejected (Rowe 1961; Howard et al. 1972; Shimizu et al. 1980; Marsh
1988; Yamaguchi 1995). Norway rats in trials preferred salty and sweet tastes
over sour and bitter ones (Karasawa & Muto 1978; Kolody et al. 1993). The most
attractive concentrations of sugars have also been assessed in various trials.
Howard et al. (1972) recommended 64 g/L in liquid baits for wild-caught and
laboratory Norway rats, while Smythe (1976) recommended 1–5% sucrose by
weight. Other authors have recommended higher concentrations (Collier &
Bolles 1968). When given the choice between sugar on its own and flour,
Norway rats consumed only small amounts of the sugar (Barnett 1956). Inverted
sugars like maltose, dextrose, fructose and levulose also are acceptable to
rodents (Smythe 1976). Of the artificial sweeteners, saccharin was favoured by
laboratory rats over cyclamate, while wild Norway and ship rats preferred
glucose to saccharin (Wagner 1971). Sugars also help preserve the baits,
potentially increasing shelf- and field-life, but also increase bait palatability to
invertebrates and reptiles (J. Russell, Auckland University, pers. comm.).
Oils can be effective additives. Meehan (1984) found that the higher the level of
oil in bait, the more readily it was taken. Mice have exhibited a preference for
high-fat foods (Imiazumi et al. 2001) and rats have an appetite for dietary fats
and oil (Elizalde & Sclafani 1990; Ramirez 1993). Glycerin, corn oil, arachis oil
and mineral oil were more palatable to mice than olive, linseed or cod-liver oils
(Rowe et al. 1974). Groundnut oil probably has a neutral flavour to rodents
(neither attractive nor repellent), but may act to mask the flavour of cereals to
which rats have developed bait shyness (Bhardwaj & Khan 1979a, b).
In conjunction with gur, groundnut oil increased bait consumption by mice
more than just the gur alone (Pathak & Saxena 1995). Olive oil enhanced the
acceptance of baits to male ship rats in no-choice tests, while soybean oil,
sunflower oil, mustard oil, groundnut oil and coconut oils were all preferred
over plain bait in choice tests, and groundnut oil was preferred over coconut
and mustard oils (Ahmad et al. 1994). However, in the same study, female rats
preferred coconut, mustard and, to some extent, sunflower and soybean oil in
mixed diets. In a study in the USA, coconut, peanut and corn oils were most
prefered by Norway rats, whilst corn oil was preferred over peanut oil by black
rats (Meehan 1984). In another study, adhesive oils reduced palatability of oats
to all three species of rat tested (Pank 1976).
12 Clapperton—Rodent behaviour in relation to control devices
3.1.3 Other additives and lures
Mice in a study exhibited a preference for monosodium glutamate (MSG) and
NaCl (salt), but more so for sugars (Yamaguchi 1995). On Thevenard Island
(Australia), mice selected parrot seed coated with agar more often than either
the seed alone or seed coated with wax (Moro 2002). The addition of salt to
these baits increased bait consumption. Also in Australia, fishmeal was a
successful additive to bait for mice (Robards & Saunders 1998; Jacobs et al.
2003). These authors listed a range of other additives that made no difference to
consumption, including chocolate, cheese, aniseed, peanut oil and honey. By
contrast, chocolate is used elsewhere as an effective trap attractant for mice
(author, pers. obs.), to such an extent that UK researchers have developed a
chocolate mousetrap (Singh 2003). The addition of 2% onion pulp (but not
garlic, ginger or tulsi) improved consumption of bajra flour by by mice in India
(Saxena et al. 1995).
Egg yolk and yeast were successful additives to poison baits for wild-caught ship
rats in Pakistan, more so than minced meat, egg shell, sheep blood or chicken
blood (Shafi et al. 1990). Conversely, egg shell ranked the highest, then egg
yolk, yeast and minced meat in field trials in Pakistan (Pervez et al. 1999).
Toasted coconut has been used successfully as bait in traps in Rarotonga
(Robertson et al. 1998).
A bait type often used for rats in New Zealand is peanut butter and rolled oats,
while the hazelnut spread ‘Nutella’ has been successful with Norway rats
(J. Russell, pers. comm.). On Browns Island, Hauraki Gulf, Auckland, cheese,
chocolate and soap were preferred (in that order) over wax and oiled wood by
Norway rats (Weihong et al. 1999). Tabuchi et al. (1991) listed black pepper,
milk and coffee as highly preferrred food-related odours; while nut,
peppermint, plum, orange and cheese also elicited a bar-pressing response from
rats. Smythe (1976) suggested that some additives act as ‘curiosity enhancers’ to
rodents and mentioned, in particular, a ‘powerful, persistent synthetic grape
flavour’. This was effective when used as a coating for plastic bags containing
the baits, but not when added into the bait. Raw fish and beef, dried dog food,
coconut oil, fresh or dried blood, chicken offal, cinnamaldehyde, raspberry,
aniseed and other commercial products have all been attributed with attractive
properties for Norway rats (Bull 1972). Shafi et al. (1992) found that yeast was
the most palatable additive to flour/rice baits, followed by egg shell, with egg
yolk, sheep and chicken blood and minced meat being less preferred. Schisla et
al. (1970) described the success of ‘Dexide’—a carbohydrate with flavour
material—that increased the consumption and efficacy of warfarin to mice, ship
rats and Norway rats. Salt and MSG are variable in their effect, and were disliked
at concentrations above 0.5% (Ohara & Naim 1977; Marsh 1986, 1988; Kolodiy
et al. 1993). Female rats consumed more salt than male rats (Flynn et al. 1993).
McFadden (1984) listed aniseed, banana, coconut, clove, eucalyptus and vanilla
as acceptable lures for kiore. Veitch (1995) found that kiore preferred Rentokil
Rid Rat baits that contained 7.5 ml/L of sucaryl over the standard baits that
contained vanilla and carbon disulphide, and those with chocolate and oil, or
coconut or vegetable oil.
13Science for Conservation 263
3.1.4 Formulations
In preliminary bait trials with wild-caught mice, O’Connor & Booth (2001) found
that PESTOFF® and Talon®50WB were more palatable and effective than
Racumin® or Talon®20P. PESTOFF®20R was, however, less palatable to mice from
Mokoia Island than standard Challenge diet (Cleghorn & Griffiths 2002). Wild-
caught mice found both non-toxic and toxic Talon®20P cereal pellets more
palatable than the RS5 cereal pellets or fishmeal pelleted ‘cat baits’ tested by
Morgan et al. (1996), presented either in a simulated aerial drop or in bait
stations. Talon wax blocks were preferred over kibbled wheat, poultry pellets
and Mapua pellets by mice on Mana Island, Wellington (Todd & Miskelly unpubl.
report cited in Cleghorn & Griffiths 2002). Talon wax blocks controlled mice on
Varanus Island, Australia (J. Angus, pers. comm. in Moro 2002).
Ship rats wild-caught from poultry sheds in India preferred freshly-prepared
formulations of Quintox® in a white flour/sugar/groundnut oil mix over comm-
ercially available Quintox® cake and pellets (Saini & Parshad 1992).
Airey & O’Connor (2003) found Talon® 50WB and Storm® wax blocks had low
palatability when presented to wild-caught Norway rats, and resulted in low
mortality. RS5 pellets and Talon®20P pellets were both preferred over fishmeal
cat pellets by wild-caught ship rats (Morgan et al. 1996). Storm was effective
against kiore on Double Island (McFadden 1992), as was Talon®20P on Burgess
Island (McFadden & Greene 1994).
Bait formulations often contain wax to enhance bait longevity and water-
resistance (O’Connor & Eason 2000). Symthe (1976) cautioned that rats in
Hawaii were averse to wax, and that waxes can vary in hardness. Norway rats on
the Noises Islands found ‘too much’ wax unattractive (Moors 1985a). Ross et al.
(2000) tested Pestoff baits with and without an unspecified additive and found
that the additive had no effect on palatability. The pelleted Pestoff formulation
was more palatable than the block formulation, and also more palatable than
Ditrac Blox.
Adhesives may be needed to hold the poison onto the bait, especially in aerial
operations. Pank (1976) found that zinc phosphide baits containing Alcolec S
were more effective than those containing corn oil.
3.1.5 Hardness
Hardness affects bait preference of rodents. Smythe (1976) suggested that
rodents will gnaw on anything, but baits with a hardness between that of soft
wheat and water-soaked corn appeared to be optimum. Ford (1977) found that
increasing hardness of diet reduced food wastage by mice and rats, that less
wastage occurred when they were fed pellets made from finely ground
materials (an effect that was not related to hardness), and that apparent food
consumption increased with the softness of the diet. Robards & Saunders
(1998) found that mice preferred soft wheat varieties. Dehusking of whole
grains by rodents can lead to the removal of the poison and thus lower efficacy
(Smythe 1976). McFadden (1984) commented that kibbled grains are more
practical than whole grains, as they allowed the poison to be absorbed into the
kernel. Similarly, both laboratory Norway rats and wild-caught ship rats have
been observed to leave the skin of carrots (author, pers. obs.).
14 Clapperton—Rodent behaviour in relation to control devices
3.1.6 Wrappings
Wrapped bait is often left on islands after eradication programmes as a security
against possible rodent survivors (Towns et al. 1994). Rodents can easily chew
through paper, plastic and ‘fiber’ (e.g. Shumake et al. 2000). However,
wrapping bait in tinfoil or in ziplock plastic bags reduced its palatability and
efficacy to mice (Brown 1993) and to Norway rats in trials (Airey & O’Connor
2003).
3.1.7 Colour
The addition of green dye had no effect on the consumption of wheat by mice
(Robards & Saunders 1998). McFadden (1984) mentioned a trial in which green
dye appeared to reduce the palatability of baits for kiore. Meehan (1984) stated
that ‘rats and mice are almost certainly colour blind, but yellow and green are
more “attractive” as they are seen as a very light grey’. Mice can discriminate
amongst colours, and laboratory mice preferred white cages over black, green
and, particularly, red ones (Walton 1933a, b; Sherwin & Glen 2003).
3.1.8 Gnaw sticks
Gnaw sticks are often used to determine the presence of rodents (e.g. Hook &
Todd 1992; Jansen 1993; Adams 1997; Shaw 1997; Garcia et al. 2002). Typically,
they are made of wood soaked in vegetable oil. Wax or cereal/wax blocks,
candles, chocolate and soap are also sometimes used (Towns et al. 1994, 1995;
Brown 1997; Nelson et al. 2002; Veitch 2002d). There have been no specific
studies comparing the attractiveness or ‘gnaw-ability’ of different sorts of gnaw
sticks.
3 . 2 M E A L S I Z E
The study by Mutze (1991) on turnover rates in wild mice indicated that mice
need to eat 17% of their body mass each day to maintain that mass. Mice are
considered to be light and intermittent feeders compared with rats (Crowcroft
& Jeffers 1961).
Clark (1982) observed that meals of ship rats tend to be dominated by one food.
Wild-caught ship rats in captivity consumed an average 14–18 g of pellets per
day (plus a slice of apple) (B.K. Clapperton et al., unpubl. data).
Adult Norway rats have exhibited a preference for food particles 0.4 to 0.7 cm
in diameter (Smythe 1976; Lund 1988b—diameter given in mm, presumably in
error). This appears to be the size of particle most suitable for a rat to hold in its
forepaws while eating. Larger-sized pieces may be hoarded by some rats. Daily
intake of different foods can vary greatly (Barnett 1956). A medium-sized
Norway rat can take six to eight grains of wheat in its mouth at one time,
making a mouthful weighing about 2.1 g. In one study, adult laboratory rats ate,
on average, about 19 g of pellets per day (B.K. Clapperton et al., unpubl. data).
Laboratory rats in one study had three or four distinct feeding bouts, eating an
estimated 2.5–6 g during each bout (Roger Quy, Central Science Laboratory,
MAFF, UK, pers. comm.); while in another study they averaged nine or ten
15Science for Conservation 263
meals per night, eating an average of 2.3 g per meal (Zorrilla et al. 2005). Wild
rats tend to have shorter meals than laboratory rats, visiting food sites more
frequently but for shorter periods of time (Barnett et al. 1978). In Norway rats,
differences in meal size are attributable to differences in sex, size and
reproductive status. Females forage in many short visits, while males use fewer,
longer visits (Inglis et al. 1996). Shepherd & Inglis (1987) found that a pregnant
or lactating female ate the most and her meals were longer and larger than those
of the males; but her feeding rate was no greater. The mean amounts eaten by
rats in that study varied between 16.3 and 84.6 g/day. The number of meals
varied from 5 to 11 per day. Food intake is thus adjusted to calorific expenditure
(Macdonald et al. 1999b).
Differences in the rate of feeding or the number and size of meals amongst
individual Norway rats imply that there are likely to be differences between
individuals in susceptibility to poison shyness resulting from ingestion of sub-
lethal doses (Shepherd & Inglis 1987).
3 . 3 N E O P H O B I A
The neophobic response can be one of the most pertinent obstacles to efficient
rat control (Lund 1988a). Barnett (1958) defined neophobia as the avoidance of
an unfamiliar object in a familiar place. It causes problems in poisoning
programmes because neophobic animals will avoid new foods and even foods
previously eaten if they are placed on or in a novel object (Barnett 1988). The
response varies not only between species (see below) but also between
populations of the same species (Mitchell et al. 1977) and between individual
animals (Cowan & Barnett 1975; Cowan 1977a). The phenomenon of
neophobia is reviewed by Brigham & Sibley (1999).
Some researchers have classed mice as neophilic, i.e. that they have a tendency
to approach unfamiliar places or objects (Chitty 1954; Barnett 1988), but other
researchers dissagree. Misslin & Ropartz (1981) found that a novel object placed
in a familiar environment did, in fact, release avoidance and burying responses
in laboratory mice. Kronenberger & Médioni (1985) demonstrated a greater
level of neophobia in wild mice than in laboratory mice. Wolfe (1969) and
Connor (1975) also found that captive wild mice developed a weak neophobic
response. However, the same authors pointed out that the very pronounced,
long-lasting avoidance behaviour of wild Rattus species is essentially absent in
wild Mus. Mice can be quite cautious about taking new baits, and use sampling
to test new foods (Chitty 1954; Brown 1993). But one study found that in cereal
crops baiting success was not improved by pre-baiting (Mutze 1989). These
studies also recommended that baiting success would be improved if bait
stations were moved around (see also Berry 1981); although Ajao & Hurst
(1992) found that mice preferred to feed from the same station over
consecutive nights. Mice are drawn to new feeding sites (Crowcroft 1959; Berry
1981; Rowe 1981). Niemeyer (2002) recommended that clearing of vegetation
in front of mouse traps attracts mice to investigate the area. In Australia, mice
readily enter live-capture traps on the first night traps are placed in fields.
However, there was significant heterogeneity in trappability over seven
consecutive nights (Davis et al. 2003).
16 Clapperton—Rodent behaviour in relation to control devices
Ship rats living in close association with people show neophobia, although there
is also some conflicting evidence (Meehan 1984). Cowan (1976) demonstrated
how changing from a familiar food basket to a novel one or moving the familiar
basket to an unfamiliar position, evoked ‘new object reaction’ in ship rats.
Altering the smell of the basket or presenting a new food in it did not evoke
avoidance. It may take several weeks for ship rats to enter bait stations (Howard
1987), or only 1–2 days (Watson 1954; Advani & Idris 1982). It is not known
whether or not truly wild populations are less neophobic because of their long
period of time with no association with people.
Commensal Norway rats are considered to be particularly neophobic (Barnett &
Cowan 1976; Cowan 1977a; Meehan 1984; Moors et al. 1992). This makes them
difficult to trap or to attract into bait stations. Adult females can be particularly
difficult (Thorsen et al. 2000). Lund (1988a) discussed the issue of neophobia in
relation to baiting techniques for rats, and recommended that bait stations be
placed close to a runway, not directly on it (citing Howard 1986a, b), and
should never be moved during a control period. Inglis et al. (1996)
recommended that baits should be covered by materials already present at the
site, and that use of natural holes or other natural sources of protection for
baits, rather than man-made bait stations, can reduce the problem of neophobia.
Establishing permanent bait stations and/or pre-feeding the target rats with
familiar highly palatable foods are suggested ways of mitigating the effects of
neophobia (Inglis et al. 1996). Even small differences in the appearance or
construction of bait stations, or in their odour, may be detected by rats.
Shepherd & Inglis (1987) demonstrated the importance of addressing the
problem of neophobia. In that study, captured commensal Norway rats ate
more difenacoum bait in a familiar container than their standard diet in a novel
feeder. This result indicates that neophobia towards a palatable food, even one
containing poison, is likely to be transient compared with the neophobia
towards a new object such as a bait station (see also Inglis et al. 1996). Feeding
from novel food containers can be delayed by several days, while feeding on
novel foods normally occurs towards the end of the first night (Brunton 1995).
Inglis et al (1996) calculated that the introduction of novel bait containers
doubled the number of days needed to accumulate a lethal dose for
brodifacoum (1 day to 2 days), and increased it 14-fold for difenacoum (1 day to
14 days). Norway rat populations isolated from human contact for many
generations on Breaksea and Hawea Islands did not appear to be neophobic
(Taylor & Thomas 1989, 1993). Neophobia may also be reduced in individuals
infected with the parasite Toxoplasma gondii (Macdonald et al. 1999a, b).
Inglis et al. (1996) found no sex differences in the degress of neophobia to
novel foods.
There is little information available about neophobia in kiore. Moors et al.
(1992) stated that kiore may even be attracted to new objects, but Harrison &
Woodville (1950) mentioned avoidance of a new food container by R. exulans
living as house-rats in Burma. Nelson et al. (2002) suggested neophobia as a
possible reason for the failure of Polynesian rats in Hawaii to use bait stations.
17Science for Conservation 263
3 . 4 F E E D I N G B E H A V I O U R
Mice may visit many feeding locations during a single foray (Crowcroft & Jeffers
1961). They appear to feed quite randomly. Although a few feeding areas may
be heavily exploited during the course of one night, these sites vary from night
to night (Meehan 1984). Mice have been described as light and erratic feeders,
making it difficult to ensure that each individual receives a lethal dose of poison
(Rowe 1973). For example, a high degree of variability in Pestoff 20R bait
consumption was recorded between individual mice from Mokoia Island
(Cleghorn & Griffiths 2002).
Ewer (1971) describes the eating, prey killing and drinking behaviour of ship
rats. Notably, they are very adept at manipulating food particles, and perching
on their haunches or clinging to branches. There are photographs of a rat sitting
on a 1.6-mm diameter wire, ‘fishing’ up a nut on a string and eating it while still
perched on the wire.
Both wild and laboratory Norway rats show marked exploratory and sampling
behaviour (Barnett 1956). When unfamiliar foods are provided to Norway rats
in familiar conditions, they are sampled during the first feeding period (Barnett
1956). The amount eaten then is not a good indicator of preference when
feeding has stabilised. This stabilising usually takes 1 or 2 days. Both adult and
juvenile rats exhibit sampling behaviour, the only difference being that adult
rats spill less food (Barnett 1956). Young rats do a lot of sampling and
exploration that could lead them to food sources (Barnett 1956). Sampling can
result in the change from feeding on one food to another or from one feeding
site to another (Barnett 1956). Such changes take several days in wild Norway
rats (Barnett & Spencer 1953a). When provided with a range of unfamiliar
foods, wild Norway rats do not sample among them in a manner that would
facilitate identification of any toxin present (Beck et al. 1988).
Barnett (1956) observed Norway rats licking their food-covered forepaws and
even the mouths of other rats. Young that were still suckling licked the paws
and mouth of the mother. Norway rats will sit back on their haunches and hold
grain in their front paws (Meehan 1984). Mice will pick up a grain in their front
paws and dehusk and eat it rather like they were peeling and eating a banana
(Meehan 1984).
There have been many studies of social facilitation of feeding in rats. Norway
rats follow trails left by other rats to find food (Galef & Buckley 1996). Cues
transmitted from a mother to her pups during the nursing period are sufficient
to determine the dietary preference of the young at weaning (Galef & Clark
1972; Valsecchi et al. 1993). Barnett (1956) noted that young Norway rats tend
to orientate themselves towards their mother, thus being led indirectly to food
sources. No evidence was found of deliberate guidance by mothers. Young rats
stay close to the adults so they tend to eat what the adults eat, and this becomes
their familiar diet (Galef & Clark 1971; Galef 1977). Naive rats will choose an
unfamiliar food after observing another rat feeding on that food (Posadas-
Andrews & Roper 1983; Galef et al. 1984; Strupp & Levitsky 1984; Galef &
Whiskin 2000, 2001). Mice also learn food preferences from observing other
mice feeding (Valsecchi et al. 1996). Food preferences in Norway rats can also
be mediated by odour cues left at feeding sites by conspecifics (Galef & Heiber
18 Clapperton—Rodent behaviour in relation to control devices
1976; Laland & Plotkin 1991), but the effect is not so pronounced in wild mice
(Valsecchi et al. 1966). Lavin et al. (1980) and Bond (1984) presented data that
support the idea that a non-poisoned rat can learn to avoid a novel flavour by
perceiving the sick state of a poisoned conspecific rat and using that cue to
avoid potentially dangerous foods. However, Galef et al. (1990) failed to
provide any evidence that naive observer rats will learn to avoid a food as a
result of interacting with demonstrator rats that had eaten the food and
exhibited symptoms of toxicosis. There is evidence that rat foetuses are able to
learn odour aversions (Smotherman 1982).
Mice (Ylonen et al. 2002) and Norway rats (Barnett & Spencer 1953a) prefer to
feed at sites close to cover. Norway rats will drag food items to cover unless the
food is too heavy, or they can feed undisturbed (Barnett & Spencer 1953a).
Enderpols et al. (2003) found that farmers who complied with a prescribed bait
station placement plan were most likely to achieve complete eradication of rats.
Bait acceptance levels in Norway rats on farms were highest in bait stations
located at specific structural elements on a farm which were the sites of highest
rat activity (Endepols & Klemann 2004), and social interactions also affected
choice of bait stations (Klemann & Pelz 2005). Macdonald et al. (1999b)
discussed the role of predators in the feeding behaviour of rats. Hoarding is
another aspect of feeding behaviour that can influence bait take. Sheikher &
Malhi (1983) found no evidence of hoarding by mice, but Naumov (1940)
described how mice in the Ukraine store food for the winter. Norway rats will
hoard food after initial bouts of feeding if they are hungry (Barnett & Spencer
1951; Fantino & Cabanac 1980; Wallace 2003). Some types of food are more
likely to be hoarded than others (Barnett & Spencer 1951). Food size, number of
feeding sites, distance to the burrow and group size all influence food-carrying
behaviour (Whishaw & Tomie 1989; Whishaw et al. 1989; Whishaw &
Dringenberg 1991; Thullier et al. 1992; Nakatsuyama & Fujita 1995). Females,
especially while lactating, are more likely to hoard than males (Boice 1977;
Meehan 1984). Ship rats do not like to feed far from shelter and will hoard food
more frequently than kiore (McCartney 1972). Not all stored food is eaten—
food caches have been found full of fungus (Meehan 1984). Veitch (2002a)
suggested that food hoarded by Norway rats on Browns Island was then
available to mice after the rats had died. Kiore will also hoard poison pellets
(Cash & Gaze 2000). McKenzie (1993) noted kiore on Motuopao Island nesting
in grass close to bait stations and feeding at regular intervals on the bait.
3 . 5 S O C I A L B E H A V I O U R
Wolff (2003) described rodent behaviour systems as complex, variable and
adapted to high reproductive rates and marked changes in density (see also
Berry 1981).
Social behaviour can influence which animals have access to bait stations. In
commensal situations, large numbers of rats may use a single bait station
(Shorten 1954). But in a captive Norway rat colony, it was observed that there
was usually a ‘pioneer’ rat that regularly appeared first in a feeding period
(Barnett & Spencer 1951). Subordinate mice (Rowe 1973) and Norway rats
(Berdoy 1991) fed when dominant animals were inactive. Similarly, Drickamer
19Science for Conservation 263
& Springer (1998) found that while there were no significant differences in
nocturnal activity patterns by age or sex, subordinate male mice were active
early in the night and dominant males were active later. Dubock (1982)
suggested that socially inferior rats might only be allowed to feed from a bait
station during the later stage of a poison operation, as they are excluded by
dominant individuals. Shepherd & Inglis (1987) also found that a dominant
female Norway rat could deter even the males from using the same food source.
Taylor & Thomas (1993) advocated the use of permanent bait stations so that
less-dominant individual Norway rats could learn from others to access the bait.
Norway rats will sometimes feed together at bait stations (J. Russell, pers.
comm.). This group feeding gives individuals a degree of protection from
predators (Roger Quy, pers. comm.). Ship rats are more gregarious and less
aggressive than kiore, relying more on grooming and stereotyped agonistic
postures (McCartney 1972).
3 . 6 M O V E M E N T S A N D H O M E R A N G E
Meehan (1984) summarised the pre-1980s literature on movements of rats and
mice. Movements and home ranges of rodents in New Zealand have been
summarised by Atkinson & Moller (1990), Innes (1990), Moors (1990) and
Murphy & Pickard (1990). Gliwicz (1980) characterised island populations of
rodents (bank voles and deer mice) as having smaller home ranges than in open
systems. Norway rats can climb trees and ship rats and mice will jump and climb
to get to food (Timm & Salmon 1988).
There are numerous references from around the world to movements of mice
(Young et al. 1952; Brown 1953; Pearson 1963; DeLong 1967; Tomich 1970;
Berry & Jakobson 1974; Nikitina et al. 1976; Twigg et al. 1991, 2002). The most
notable findings are reported in the following text. Mice tend not to move great
distances. In an agricultural setting in Australia, one third of the mice were
caught in the same trap location, and the maximum recorded movement was
60 m (Twigg et al. 2002). Most estimates of average home range size for free-
ranging wild mice vary between 0.0035 and 8.024 ha (Lidicker 1966; Fitzgerald
et al. 1981; Sage 1981; Krebs et al. 1995; Chambers et al. 2000). In the
Orongorongo Valley, New Zealand, mice would visit many parts of their ranges
in one night (Fitzgerald et al. 1981). Males tend to travel further than females
(Lidicker 1966; Quadagno 1968; Tomich 1970; Hackmann et al. 1980; Mikesic &
Drickamer 1992), but Fitzgerald et al. (1981) found that female home ranges
sometimes matched those of males. Female home range size can increase in
winter (Lidicker 1966). In feral mice in San Francisco, movement peaks
occurred in the coldest part of winter, during the breeding season and when the
population was nearly extinct (Lidicker 1966). In Australian wheatfields, ranges
of mice could be ten times larger outside of the breeding season than during it
(Krebs et al. 1995). Home range size may also be affected by competition from
other rodents (Quadagno 1968). Mice seldom cross roads (Kozel & Fleharty
1979; Wilkins 1982), and they prefer to stay close to cover (Gray et al. 2000).
Female mice stay near the nest around parturition and thereafter spend more
and more time away from it (Barnett & McEwan 1973). Usually juveniles
disperse, setting up territories in unoccupied space (DeLong 1967; Mackintosh
20 Clapperton—Rodent behaviour in relation to control devices
1981), but older mice will move if habitat conditions deteriorate (Newsome
1969a, b). Mice living in refuge habitat (along fencelines) in Australian
wheatfields would make foraging movements extending to about 20–30 m into
the crop (Jacob et al. 2004). Successful island eradications of mice have used
bait station spacings of 25 or 50 m (Hook & Todd 1992; Brown 1993). Twigg et
al. (1991) recommended bait station spacings of no more than 20 m in
Australian soybean crops. Moro (2001) found that mouse densities declined
more on grids with bait stations spaced every 10 m than on grids baited every
20 m; and according to Moro (2001), manufacturer recommendations for the
use of Talon for mouse control is for baits to be no more than 3 m apart.
Ship rat movements are, typically, also small. Estimates of average movements
between captures vary from 18 to 174 m (Spencer & Davis 1950; Watson 1951;
LaVoie et al. 1970; Daniel 1972; Temme 1973; Innes & Skipworth 1983; Dowding
& Murphy 1994). In New Zealand forests, ship rats have been recorded as evenly
(Innes & Skipworth 1983) or patchily distributed (Dowding & Murphy 1994) in
home ranges averaging about 1 ha for males and smaller for females (Tomich
1970; Innes & Skipworth 1983; Hickson et al. 1986; Dowding & Murphy 1994). In
Fiordland, in March 2000, three male ship rats had home ranges of 7.5, 9.1 and
11.4 ha, while two females had home ranges of 0.89 and 0.27 ha (Pryde et al.
2005). Home range sizes in the Orongorongo Valley estimated by Daniel (1972)
were much smaller (0.17 ha for males and 0.08 ha for females). Ranges are
sometimes exclusive, but Dowding & Murphy (1994) found substantial overlap in
ranges, both between and within sexes, and den sharing. Male ranges may
increase during the breeding season. In Tenerife, Canary Islands, ship rats were
more active along roads than in other parts of forests (Delgado et al. 2001). Roads
that ran on forest ridges and slopes were used more than those in ravine beds in
laurel forest, but there was no topographical difference in road use in pine forest.
At North Head, New South Wales, ship rats favoured habitat with dense
understorey, especially with enhanced leaf litter (Cox et al. 2000). On Macquarie
Island, ship rats were found in areas with extensive stands of tussock, including
beaches, raised coastal terraces, coastal hill slopes, coastal ridge tops, coastal
rock stands, and stream courses (Pye et al. 1999). The tussock fringes of stream
courses were important dispersal corridors into the inner areas of the island.
A bait station spacing of 100 m is considered suitable for ship rats (Innes 1995);
although, if home ranges are less than 1 ha (as is the case for most females), not all
rats will have access to a bait station in their home range at this spacing. However,
as neighbouring rats are removed by the poisoning, the remaining rats are likely
to move into the unoccupied space (Innes 1990).
Norway rats can move many kilometres, but average movements of radio-
tracked rats in arable land were 340 m for females and 660 m for males (Taylor
& Quy 1978). The tracked rats usually kept to hedgerows, but some crossed
open areas for up to 500 m. These movements were considered to be changes in
home sites, and males made them every 7 days and females every 14 days
(Taylor 1978). Captive rats systematically patrolled their home ranges (Cowan
1977b). Norway rats living near human food depots moved shorter distances
than the above stated (Davis et al. 1948; Hardy & Taylor 1979; Hartley & Bishop
1979). Norway rats studied by Davis et al. (1948) and Kemper (1960, cited in
Davis 1953) moved up to about 45 m between places of shelter and food.
Kunkel (1989) noted that home range size in urban parks was dependent on the
21Science for Conservation 263
proximity of burrows to food sources. On the Noises Islands, Norway rats
travelled widely (average distance 113 m) between successive captures, with
males moving further than females (Moors 1985b). Over 2–5 nights, Norway
rats on Whale Island moved on average 72 m (Bettesworth 1972). Distances
travelled and home ranges of Norway rats increased as food became more
dispersed (Hardy & Taylor 1979). Gibson (1973) studied a Norway rat burrow
system near Christchurch. The removal of two lactating females from the
colony resulted in the nestlings moving beyond their burrows and subsequently
being captured. Norway rats on the islands of South Georgia were found mostly
in dense stands of coastal tussock grasslands, with burrows excavated out of the
peat (Pye & Bonner 1980). Hartley & Bishop (1979) made the observation that
Norway rat infestations in hedges were always associated with streams. Norway
rat home ranges on Kapiti Island averaged 5.78 ha for males and 5.13 ha for one
female (Bramley 1999). Home range lengths averaged 438.7 m (males) and
459 m (females). Successful island eradications of Norway rats have used bait
station spacings of 50 or 100 m (Moors 1985a; Taylor & Thomas 1993; Kaiser et
al. 1997; Taylor et al. 2000). Newly arrived on Frégate Island, a Norway rat
settled in one area, around which its offspring also settled (Thorsen et al. 2000).
Most captures of rats on this island were in a 75 × 60 m area until 8 months after
the invasion.
Kiore nest and feed in trees (Daniel 1969; McCartney 1970; Williams 1973;
Moors et al. 1992), and make arboreal runways through coconut fronds
(McCartney 1970). However, they are only occasionally captured in the forest
canopy (Stone 1985; Sugihara 1997). Average kiore home ranges on Kapiti
Island were much smaller than those of Norway rats (0.14 ha for males and
0.18 ha for females). Range lengths were 51.8 m (males) and 67.2 m (females)
(Bramley 1999). The kiore were in the areas of denser vegetation, where they
may not easily come in contact with poison baits (Bramley 1999). Kiore on
Stewart Island were most abundant in manuka and riparian shrubland, habitats
with dense ground cover (Harper et al. 2005). Home ranges of kiore on Tiritiri
Matangi Island averaged 37–60 m but were very variable in size (Nicholas 1982).
Size and shape of kiore home ranges varied with habitat and population density
in Hawaii (Jackson & Strecker 1962; Nass 1977, but see Wirtz 1972). Dwyer
(1978) found segregation of males and females, and amongst age classes. Male
kiore in New Zealand tend to move further than females and adults further than
juveniles (Moller 1977; Nicholas 1982). This has also been shown to be the case
in the Pacific and Asia (Jackson & Strecker 1962; Tomich 1970; Tamarin &
Malecha 1971; Wirtz 1972; Lindsey et al. 1973; Williams 1974; Nass 1977;
Dwyer 1978). In sugarcane, average distances kiore moved between successive
captures was about 35 m (Lindsey et al. 1973). Successful island eradications of
kiore have used bait station spacings of 50 m (McFadden & Towns 1991;
McKenzie 1993; McFadden 1997; Cash & Gaze 2000). The 100-m spacing of bait
stations on Coppermine Island may have contributed to the failure of the kiore
eradication there (McFadden 1997). Bait stations 20–25 m apart may be
necessary for kiore (Bramley 1999).
22 Clapperton—Rodent behaviour in relation to control devices
3 . 7 T E R R I T O R I A L I T Y
Mice have a flexible form of territoriality, dependent on the distribution of
resources and population dynamics (Myers 1974; Lloyd 1975; Hackmann et al.
1980; Maly et al. 1985; Hurst 1987a; Krebs et al. 1995b; Chambers et al. 2000;
Gray et al. 2000, 2002). The apparent difference in social organisation between
field and commensal rodents seems to be due primarily to the fact that food is
much more evenly distributed in most field situations. In commensal situations,
mice form cohesive social groups, or demes, that defend a communal territory
(Crowcroft 1955; Crowcroft & Rowe 1963; Lidicker 1976; Mackintosh 1981;
Singleton 1983). Territory boundaries tend to form where there are distinctive
physical features (Mackintosh 1981; Singleton & Hay 1983). When mice are at
high densities in agricultural landscapes, home ranges overlap, and at the end of
the breeding season the mice become nomadic (Krebs et al. 1995a, b; Chambers
et al. 2000). In evergreen New Zealand forests, where mouse densities are low,
there is exclusive use of space by both sexes, and territorial defence (Fitzgerald
et al. 1981), although mice did maintain group territories in the Marlborough
Sounds (Murphy & Pickard 1990).
Ship rats in New Zealand forest generally do not live in colonies like commensal
rats (Hooker & Innes 1995), although Dowding & Murphy (1994) recorded them
denning together. Adult females tend to occupy exclusive areas in the breeding
season (Innes & Skipworth 1983; Hickson et al. 1986), but not always, and rats
have been observed together, usually one following another. There has been no
published study of territoriality of Norway rats or kiore in New Zealand.
Macdonald et al. (1999b) summarised the social system of commensal Norway
rats in Britain. Where resources were scarce or scattered, males appeared to
maintain exclusive ranges, with access to numerous females. Groups developed
around reliable food supplies. Social organisation in a captive colony of kiore was
described as hierarchical, with females dominant over males (Davis 1979).
Rodents, particularly kiore, probably avoid other rodent species, but habitat
structure is more important than direct competition in determining their
distribution (Dick 1985; Bramley 1999). Norway rats may, however, prey on kiore
(Bramley 1999). It has been suggested that interference from Norway rats may
cause kiore to feed more up in trees (Atkinson & Moller 1990). Ship rats may
dominate kiore (Russell & Clout 2004), and the two species compete for nest sites
(McCartney 1970). Ship rats have been observed killing mice (Ewer 1971).
3 . 8 R E S P O N S E S T O B A I T S T A T I O N S
A lot of the thrust of rodent bait station development has been not for the
improvement of efficacy but, rather, for the reduction of pesticide hazards
(Kaukeinen 1989; Jacobs 1990). Some issues of concern elsewhere are not
necessarily relevant to rodent control on New Zealand islands. Obviously, an
assessment of non-target risks will affect bait station design. The entrance hole
should be just large enough for the largest target rodent to enter (Lund 1988b).
Howard (1987) noted that a station should be large enough for the target
rodents to be comfortable while feeding in the box. This is important, not just
to ensure that a visiting rodent eats plenty of bait, but also that it eats it in the
23Science for Conservation 263
box, not removing it. It is important that the interiors of bait stations are large
enough for Norway rats to sit in their preferred position on their haunches to
eat the bait (Roger Quy, pers. comm.).
Bohills et al. (1982) found that mice were more likely to consume baits inside small
bait boxes than from large boxes or open trays. Eight bait station designs tested by
Kaukeinen (1989) did not differ in mouse utilisation. In contrast, rats varied in
their use of these stations. Volfova & Stejskal (2003) found that mice preferred the
largest plastic box they tested. They suggested that the mice were opting for a ‘bed
and breakfast’ strategy. Given a choice between two stations of the same size and
shape, the mice chose one made of metal over one made of paper.
Bait stations can be made of wood, plastic or bamboo. If made of metal, Howard
(1987) recommended that they have a plastic or some other liner. Lund (1988b)
stated that wooden boxes are generally better accepted by rodents than metal
ones (see section 3.3 of this report). Bohills et al. (1982) found that mice
preferred cardboard boxes over those made of plastic. Cylinders were preferred
over triangular, but not rectangular, boxes. A study by Ajao & Hurst (1992)
found that mice took more food from cardboard stations than plastic stations of
identical design. The baffles placed inside commercial bait stations to prevent
children from reaching in may prevent group feeding by Norway rats (Roger
Quy, pers. comm.).
Corrigan & Williams (1986) descibed a PVC piping T-station designed for the
control of mice in poultry operations. Kaukeinen (1987) noted that simpler
designs were, in general, used sooner and to a greater extent by Norway rats than
more complex designs. Weihong et al. (1999) found that wire-mesh trap covers
were more often entered by Norway rats than those made of clear plastic or
galvanised iron. Erickson et al. (1990) devised an ingenious station design for ship
rats that excludes deer mice and house mice. The station is set on a central pole
that is easily climbed by the rats, but not the smaller rodents. This design could
have potential for the exclusion of other ground-dwelling non-target species.
A 20-L plastic bucket design with wooden ramps also makes use of the climbing
behaviour of ship rats for bait access (Morris 2002). Innes (1995) commented that
less bait would be wasted if bait stations for ship rats were off the ground away
from dampness on Norfolk Island. In a macadamia nut orchard in Hawaii, baits
placed in the trees were more often taken than those placed on the ground (Tobin
et al. 1997). Ship rats appeared to enter yellow ‘Nova Pipe’ stations freely (Taylor
1984). McFadden (1984) used large plastic containers with 70-mm-diameter
holes at either end. He found that kiore on Lady Alice Island entered these
containers and fed on the bait, but Norway rats on the Noises Islands were
reluctant to enter them (Moors 1985a). Spurr et al. (2005) found that captive
Norway rats preferred to enter and eat bait from wooden boxes, yellow ‘Nova
Pipe’ or black plastic boxes than larger white plastic containers.
3 . 9 O T H E R F A C T O R S
3.9.1 Behavioural resistance
This concept covers the various behavioural characteristics that make it hard to
control a rodent population that has had previous experience with poisoning. It
was defined by Brunton et al. (1993) as ‘behavioural traits which diminish a rat’s
24 Clapperton—Rodent behaviour in relation to control devices
tendency to eat palatable poison to which it otherwise has access to consume a
lethal dose’. It includes learned behaviours like the development of bait shyness
and poison avoidance through conditioned food aversion learning, and
enhanced neophobia (Brunton et al. 1993). Beyond this, Humphries et al.
(1992, 2000) have provided evidence that some populations of house mice in
Birmingham show inherited behavioural cereal bait aversion. Such innate
behaviours include neophobia and the ability to detect and recognise poison.
Bait shyness can lead to enhanced neophobia. Rats that have survived poisoning
operations are more neophobic than those never exposed to poison
(Macdonald et al. 1999b). Greaves (1994) noted that ‘avoidance behaviour,
which could be heritable, can and does reduce the efficacy of rodenticides and
may also enhance the effects of physiological resistance’ (see below).
Behavioural resistance can be exacerbated by the presence of ample alternative
foods so that the rodents are not pressured to eat the poison baits, and by other
ecological factors (Greaves et al. 1982b; Berdoy & Macdonald 1991; Quy et al.
1992; Macdonald et al. 1999b).
3.9.2 Bait shyness and poison aversion
There is a vast literature on the development of bait shyness and poison
aversion in rodents. I do not attempt a comprehensive review of the knowledge
here, but draw attention to some of the relevant literature. Early studies include
that of Richter (1953) and Rozin (1968). Some of the key papers on the
mechanisms of aversion learning include Nachman & Ashe (1973), Nachman &
Jones (1974), Nachman & Hartley (1975) and Best & Batson (1977). A number of
researchers, especially in India, have looked at the role of various food
characteristics in the development of conditioned food aversions, and aversions
to different poisons (e.g. Howard et al. 1968; Bhardwaj & Khan 1978; 1979a, b;
1980; Rao et al. 1980; Bhardwaj et al. 1984; Jain & Sarkar 1984; Naheed & Khan
1989, 1990; Singh & Saxena 1991; Zeinelabdin & Marsh 1991; Saxena & Mathur
1995; Saxena et al. 1995). Mice did not develop bait shyness to Quintox® (Twigg
& Kay 1992). Thomas & Taylor (2002) noted that either bait shyness or poison
resistance was apparent in the rat population on Ulva Island. Reviews of
aversion learning are found in Domjan et al. (1977), Domjan (1980), Garcia et
al. (1985), Lund (1988a), and Prakash (1988). Riley & Clark (1977) provide a
bibliography on conditioned taste aversion literature. Cowan et al. (1994)
recommended micro-encapsulation of poisons as a way of reducing the
formation of learned aversions, by delaying the symptoms of poisoning.
3.9.3 Resistance
Rats can also be physiologically resistant to poisons (Thijssen 1995; Taylor et al.
1996). This is a genetic trait that has been selected for over generations of
exposure to certain rodenticides (Greaves 1994; Kohn & Pelz 1999; Kohn et al.
2003). Warfarin-resistant mice, Norway rats and ship rats have been found in
England and Europe (Boyle 1960; Greaves et al. 1976; Greaves 1994). Warfarin-
resistant rats can be also resistant to difenacoum (Greaves et al. 1982a, b). The
issues of bait avoidance and the efficacy of poisons against warfarin- and
difenacoum-resistant rats were discussed by Quy et al. (1992). Cleghorn &
Griffiths (2002) found no evidence of resistance to brodifacoum in mice from
Mokoia Island.
25Science for Conservation 263
3.9.4 Odours
Odours play an important role in feeding, social and reproductive behaviour of
rodents (Bronson 1976; Hurst 1990a, b, c, 1993). They can affect rodent
responses to traps, baits and bait stations (Becker 1977; Stoddart 1983). The
odour of preferred foods and male mouse urine increased mouse investigatory
behaviour (Pennycuik & Cowan 1990), while consumption of high-fat foods by
mice was mediated by odour cues (Kinney & Antil 1996). Hurst (1987b)
proposed that urine marks may provide cues or orientation and may enhance
the rapid detection of novel objects. The odour left in traps by recent occupants
affect mice in different ways, dependent on sex, age and reproductive status
(Rowe 1970; Wuensch 1982; Drickamer 1995, 1997; Drickamer et al. 1992).
In general, though, traps scented with the odour of mouse have achieved higher
catch rates than clean traps (Temme 1980). Bait stations scented with the odour
of sexually mature mice were visited more often by male mice than clean
stations (Volfova & Stejskal 2003). As mentioned earlier, scent trails left by
conspecifics lead rats to food sites (Galef & Buckley 1996), and urinal and faecal
deposits at food sites can transmit food preferences amongst rats (Galef &
Heiber 1976; Laland & Plotkin 1991; Valsecchi et al. 1993; Selvaraj & Archunan
2002b). The bioactivity of some of the components of rat urine has been
described by Selvaraj & Archunan (2002a). Bull (1972) found that odours failed
to influence feeding activity at preferred or non-preferred sites.
Sulphur-containing compounds found in rat gland extracts can attract ship rats,
Norway rats and mice to baits. This response is concentration-dependant.
Carbon disulphide is attractive at concentrations between 0.0001% and 0.005%
but can be repellent to ship rats at 0.01% (Bean et al. 1988; Shumake & Hakim
2001; Shumake et al. 2002; Veer et al. 2002). However, Parshad (2002) reported
improved zinc phosphide bait acceptance and trapping of ship rats with the
addition of 1%. Dimethyl sulphide and dimethyl disulphide are similarly
attractive to ship rats (Veer et al. 2002). Carbon disulphide can, however,
evaporate rapidly off baits (Veitch 1995).
Mice in trials avoided human odours (Drickamer et al. 1992). Norway rats have
also been found to be responsive to human odour (Taylor et al. 1974a). Naive
rats avoided the odours of predators, but predator-experienced ship rats and
Norway rats did not (Bramley 1999), and rats in this study did not avoid feeding
stations tainted with synthetic predator odours.
3.9.5 Repellents
While a full search of the literature on repellents is outside the scope of this
review, the following information is relevant. Aniseed is thought to be repellent
to Norway rats (Barnett & Spencer 1953b). Capsacin and, to a lesser extent,
denatonium, have deterred rats from gnawing (Shumake et al. 2000). Bitrex®
has been commonly added to baits to produce a bitter taste to humans.
Kaukeinen & Buckle (1992) found that wild commensal Norway rats and mice
accepted Bitrex® at 10 ppm in Talon® and Klerat®. However, kiore on Little
Barrier Island chose Bitrex-free baits over those containing Bitrex (Veitch
2002c), and at least two eradication attempts using Bitrex have failed
(I. McFadden, pers. comm. in McClelland 2002a). Compounds added to baits as
bird repellents can reduce palatability, although cinnanamide and tannic acid
26 Clapperton—Rodent behaviour in relation to control devices
were acceptable to laboratory-bred Norway rats (Spurr et al. 2001), as were
combinations of cinnamon/Avex® (B.K. Clapperton et al. unpubl. data).
Combinations of d-pulegone/Avex® were less palatable to both rat species (B.K.
Clapperton et al., unpubl. data). Fungicides can reduce bait palatability, but
Smythe (1976) found that para-nitrophenol can be acceptable (to unspecified
rodents) at an appropriate level.
Ultrasonic sound was once heralded as a promising rat repellent system (Pinel
1972, 1974). High-intensity ultrasonic sound elicits a flight response, and rats
rapidly learn to avoid sources of noxious sound. However, while there are
ultrasonic products available for domestic use, this system is not used in large-
scale rodent control. There is no scientific evidence that ultrasonic devices are
effective, presumably because of problems with habituation and practicalities
of field application.
3.9.6 Grooming
One behavioural trait of mice that has been taken advantage of in pest control is
grooming. Poisonous dust laid on mouse runways or in holes collects on the
animals and is ingested during grooming (Rowe 1973).
3.9.7 Responses to traps
The role of residual odours on trap efficacy has been covered above (see section
3.9.4). Different species of rodents are not equally trappable—Norway rats are
comparatively difficult to trap (Taylor et al. 1974b). Individual rodents are also
not equally trappable, because of a combination of intrinsic factors and
experience (Crowcroft & Jeffers 1961; Hurst & Berreen 1985; Khan 1992).
Individual mice, especially females, can be either trap-prone or trap-shy. Males
and females can show different levels of trappability, as can adults and
subadults (Drickamer et al. 1999). Extrinsic factors (e.g. humidity, temperature
and vegetation cover) can change the relative trappability of mice (Drickamer
1999; Davis et al 2003).
3.9.8 Practical matters
Smythe (1976) and Timm & Salmon (1988) noted that baits and bait materials
are often stored with other chemicals. They can thus become tainted and
possibly unattractive to rodents. Morgan et al. (1996) showed that mixed
storage of Talon, RS5 and fishmeal baits reduced consumption of the Talon baits
by mice, but did not affect ship rat consumption of any of the baits. Smythe
(1976) also commented that baiting programmes are often ineffective because
of poor-quality bait materials, stating that rodents do not like grain that is
rodent-contaminated, dirty, old, stale or musty. Asran (1993a) found that mice
preferred fresh baits to old baits that had been infested with insects. However,
Roger Quy (pers. comm.) was surprised at the wide variety of foods eaten by
wild rodents, including some disgusting-looking or smelling foods; and Twigg et
al. (2002) found that ZP wheat bait that had been in dry storage for 3.5 years
was more effective at killing mice than fresh bait. This was attributed to the lack
of the typical strong zinc phosphide smell in the aged bait. Likewise, Reserpine
baits that had been in storage for 1–9 months were as palatable as fresh baits to
mice (Meehan 1980).
27Science for Conservation 263
Feeding by non-target species can also influence bait take. Jacob et al. (2002)
found that in bait stations designed for mice in Australia, pellet baits were
removed more by ants than by mice.
4. Discussion and conclusions
There have been few comparative studies of behavioural responses of pest
rodents to control devices. There is ample literature on rodent behaviour in
regards to medical research and psychology. Research related to pest rodents
was focused on specific pest species.
There is much information available on attractants, but there are no magical
attractants for all rodents. There is wide variability between species, between
populations and between individuals in taste preferences. As a general rule,
familiar foods with enhanced levels of sugar, fat or oil and/or salt are likely to
make acceptable baits. Various formulations are available, often containing wax
to improve environmental longevity. Soft baits are, in general, more preferred,
but can lead to more wastage. Bait size should be suitable for the feeding habits
of the target rodent.
Levels of neophobia vary amongst the four rodent species present in New
Zealand. Little is known about variation in neophobia over time, or with
population density or food supplies. Cowan (1977a) made the important point
that neophobia may have arisen as a result of selection during the development
of the commensal habitat. He proposed that isolated populations of rats, living
now in the absence of such selection, as on islands, might show little new-
object reaction. The significance of this for island re-invasion is that while rat
populations long established on islands may not show neophobia and thus may
be easy to eradicate, new invaders from commensal populations may be a lot
more wary of baits and bait stations. Alternatively, the difficulties eradicating
rats recently arrived on islands may be more due to low density reducing
competition and therefore less pressure for rats to feed on less-preferred foods
(i.e. baits).
The implication from the different feeding behaviours and neophobic responses
between rats and mice is that while rat bait stations need to be kept in one place
for many nights to overcome neophobia; for mice, a better strategy is to move
the bait stations to encourage exploration. Movement patterns of the different
species indicate that different bait station spacings may be needed, depending
upon the target species. The effectiveness of bait stations above ground level
should be assessed.
The movements of wild rats are largely the result of the two inherent (but
opposing) tendencies to explore and to avoid (Barnett 1956). The complex
interaction between different behavioural responses to food and bait stations by
various rats was well summed up by Shepherd & Inglis (1987), discussing
commensal Norway rats: ‘We have two possible answers to the question of
“Which rats do not eat the poison when a treatment fails?” The first is that it is
28 Clapperton—Rodent behaviour in relation to control devices
the subordinates, who have been excluded from the “delicious” rat bait by the
dominant animals. In this case a little perseverance should do the trick; once
the dominants have been eliminated, the subordinates will eat the bait in their
turn. The second answer is that the survivors are the dominant animals who are
most neophobic and have not been tempted away from their familiar diet. In
this case simple perseverance with the treatment is unlikely to succeed’.
Territoriality of rodents varies from species to species and with ecological
conditions. The ability of individuals in a population to access baits or bait
stations could vary with population density, or food supply. Placing of control
devices should thus be determined with reference to the socio-ecological
characteristics of the population in question.
Issues such as bait shyness and other forms of behavioural resistance obviously
play a major role in the success of ongoing rodent control operations, and there
is substantial literature on these subjects. Their application to one-off
operations on islands, however, is limited. They have application to re-invasion
by rodents. Knowledge of the history of control of populations from which re-
invaders come would allow an assessment of the significance of these
behavioural traits to eradication efforts.
The interactions between behaviour of the rodents and ecological factors will
determine the success of poison baiting. Rowe et al. (1974) concisely stated a
common theme in the literature: ‘House-mice are most difficult to control in
places where food and cover coincide and are extensive’. This message is being
heeded. Miller & Miller (1995) noted that successful island rodent eradication
programmes have been timed to coincide with low population numbers and the
cessation of breeding, and a limited food supply. According to Roger Quy (pers.
comm.): ‘The key feature determining the degree of success during control
operations is the stability of the habitat and thus the likelihood that individuals
will actively or inadvertently avoid traps, baits or bait containers’. Gray & Hurst
(1997) also stress the impact of environmental factors on the social behaviour
and, thus, spatial dispersion of mice.
No matter what behavioural challenges rodents provide, with adequate
resources, it is possible to eradicate them, at least from restricted areas. As
Elton (1940) remarked: ‘One reason why even very efficiently organised
destruction of rodents does not extinguish them is really the same reason why a
predatory animal does not wipe out its prey: when rodents become scarce
pursuit is no longer worth the expenditure of energy needed to make a kill’. But
as Rowe (1973) concluded: ‘With the mouse just such pursuit is essential if
populations are to be eradicated’.
5. Acknowledgements
I am very grateful to Roger Quy for replying in such length to my email. He
provided me with an expert overview of the issues which was essential for
making sense of all else I read. Thanks also to James Russell who provided me
with a lot of his own knowledge and an extensive bibliography, and comments
29Science for Conservation 263
on the manuscript. David Cowan, John Innes Glen Saunders, and Bruce Thomas
also promptly replied to my cries for help. The whole project would have been
impossible without the efficient assistance with librarian services from Ferne
McKenzie, who dealt with my requests that started as a cascade, rapidly turned
to a torrent and continued to trickle for quite a while! The project was funded
by the Department of Conservation (DOC Science Investigation no. 3716), and I
thank Elaine Murphy for giving me the opportunity to do this review, for
guiding me through it, and for her editorial comments. Thanks also to Grant
Singleton and an anonymous referee for their constructive criticisms.
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46 Clapperton—Rodent behaviour in relation to control devices
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47Science for Conservation 263
Appendix 1
C O M B I N A T I O N S O F W O R D S U S E D I N T H ES T N E A S Y S E A R C H E S
In some cases the words were searched for only in the title. The words were
spelt using both English and American spellings.
SEARCH FIRST TERMS AND SECOND TERMS AND THIRD TERMS
1 mouse OR mice OR Mus bait OR food preference
2 mouse OR mice OR Mus bait OR lure palatability OR attractiveness
3 mouse OR mice OR Mus bait OR food OR lure neophobia OR investigatory
OR rat OR rattus OR rodent
4 rat OR Rattus OR rodent preference OR palatability bait OR lure
OR attractiveness
5 mouse OR mice OR Mus rat bait station OR bait container
OR rattus OR rodent
6 mouse OR Mus home range OR territory OR territorial
7 mouse OR Mus OR rat OR Rattus poison OR toxin OR bait OR rodenticide aversion OR shyness
8 mouse OR rodent OR Mus eradication
9 mouse OR Mus social organisation OR spacing behaviour
10 mouse OR mice OR Mus taste OR flavour OR food preference OR choice
OR rat OR Rattus
11 mouse OR mice OR Mus meal OR bait OR food size OR quantity OR amount
OR rat OR Rattus
12 mouse OR mice OR Mus OR rat eat OR eating OR feeding OR foraging behaviour
OR Rattus OR rodent
13 rat OR Rattus social organisation OR spacing behaviour
OR home range OR territorial
14 mouse OR Mus OR rat OR Rattus invasion OR invasive behaviour
OR rodent
15 mouse OR Mus OR rat OR Rattus invasion OR invasive AND island behaviour
OR rodent
16 mouse OR Mus OR rat OR Rattus response OR bait OR baiting trap OR trapping
OR mice OR behaviour
17 mouse OR Mus OR rat OR Rattus preference OR behaviour OR sight colour
OR mice OR vision OR choice
18 mouse OR Mus OR rat OR Rattus detect OR detection NOT cell OR gene habitat OR island OR environment
OR mice OR rodent
19 mouse OR Mus OR rat OR Rattus pest OR control OR repel OR averse sound OR sonic OR ultra OR noise
OR mice OR rodent OR avoid
20 mouse OR Mus OR rat OR Rattus gnaw
OR mice OR rodent
48 Clapperton—Rodent behaviour in relation to control devices
Appendix 2
F U R T H E R B I B L I O G R A P H Y
The following references are to papers that were found during the preparation
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